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En el instante 23 de junio de 2026, 16:08:03 UTC,
-
Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Bird community structure and species responses to edges in laurel forest fragmented by narrow roads (Tenerife, Canary Islands).
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| 79 | "notes": "We examined interacting effects of habitat structure, | 79 | "notes": "We examined interacting effects of habitat structure, | ||
| 80 | topographic landscape, road edge and vehicle traffic (density and | 80 | topographic landscape, road edge and vehicle traffic (density and | ||
| 81 | noise), on bird species composition, abundance and diversity in the | 81 | noise), on bird species composition, abundance and diversity in the | ||
| 82 | laurel forest of Tenerife (Canaries). We examined multivariate habitat | 82 | laurel forest of Tenerife (Canaries). We examined multivariate habitat | ||
| 83 | and landscape factors determining bird community composition and | 83 | and landscape factors determining bird community composition and | ||
| 84 | structure, and modality of specific responses by comparing road edge | 84 | structure, and modality of specific responses by comparing road edge | ||
| 85 | vs interior zones. Abundance of breeding birds in laurel forest showed | 85 | vs interior zones. Abundance of breeding birds in laurel forest showed | ||
| 86 | slight to no increases in response to roads. Two specialized taxa, the | 86 | slight to no increases in response to roads. Two specialized taxa, the | ||
| 87 | palaeoendemic pigeon Columba bollii and Regulus regulus, revealed | 87 | palaeoendemic pigeon Columba bollii and Regulus regulus, revealed | ||
| 88 | neatest negative reductions in abundance near roads. Higher noise | 88 | neatest negative reductions in abundance near roads. Higher noise | ||
| 89 | levels, vegetation density, lower canopy closure and wood selective | 89 | levels, vegetation density, lower canopy closure and wood selective | ||
| 90 | extraction characterized roadsides. Most passerines showed moderate | 90 | extraction characterized roadsides. Most passerines showed moderate | ||
| 91 | affinity for forest edges and did not evidence decreases due to road | 91 | affinity for forest edges and did not evidence decreases due to road | ||
| 92 | proximity. The topographic landscape in these mountainous areas | 92 | proximity. The topographic landscape in these mountainous areas | ||
| 93 | strongly interacted with road edge effects to determine bird community | 93 | strongly interacted with road edge effects to determine bird community | ||
| 94 | structure. Narrow road disturbances on the laurel forest was related | 94 | structure. Narrow road disturbances on the laurel forest was related | ||
| 95 | to moderate increase in bird abundance and diversity near edges, but | 95 | to moderate increase in bird abundance and diversity near edges, but | ||
| 96 | at the cost of losing presence of forest-demanding species playing | 96 | at the cost of losing presence of forest-demanding species playing | ||
| 97 | important ecological roles.", | 97 | important ecological roles.", | ||
| 98 | "notes_translated": { | 98 | "notes_translated": { | ||
| 99 | "en": "We examined interacting effects of habitat structure, | 99 | "en": "We examined interacting effects of habitat structure, | ||
| 100 | topographic landscape, road edge and vehicle traffic (density and | 100 | topographic landscape, road edge and vehicle traffic (density and | ||
| 101 | noise), on bird species composition, abundance and diversity in the | 101 | noise), on bird species composition, abundance and diversity in the | ||
| 102 | laurel forest of Tenerife (Canaries). We examined multivariate habitat | 102 | laurel forest of Tenerife (Canaries). We examined multivariate habitat | ||
| 103 | and landscape factors determining bird community composition and | 103 | and landscape factors determining bird community composition and | ||
| 104 | structure, and modality of specific responses by comparing road edge | 104 | structure, and modality of specific responses by comparing road edge | ||
| 105 | vs interior zones. Abundance of breeding birds in laurel forest showed | 105 | vs interior zones. Abundance of breeding birds in laurel forest showed | ||
| 106 | slight to no increases in response to roads. Two specialized taxa, the | 106 | slight to no increases in response to roads. Two specialized taxa, the | ||
| 107 | palaeoendemic pigeon Columba bollii and Regulus regulus, revealed | 107 | palaeoendemic pigeon Columba bollii and Regulus regulus, revealed | ||
| 108 | neatest negative reductions in abundance near roads. Higher noise | 108 | neatest negative reductions in abundance near roads. Higher noise | ||
| 109 | levels, vegetation density, lower canopy closure and wood selective | 109 | levels, vegetation density, lower canopy closure and wood selective | ||
| 110 | extraction characterized roadsides. Most passerines showed moderate | 110 | extraction characterized roadsides. Most passerines showed moderate | ||
| 111 | affinity for forest edges and did not evidence decreases due to road | 111 | affinity for forest edges and did not evidence decreases due to road | ||
| 112 | proximity. The topographic landscape in these mountainous areas | 112 | proximity. The topographic landscape in these mountainous areas | ||
| 113 | strongly interacted with road edge effects to determine bird community | 113 | strongly interacted with road edge effects to determine bird community | ||
| 114 | structure. Narrow road disturbances on the laurel forest was related | 114 | structure. Narrow road disturbances on the laurel forest was related | ||
| 115 | to moderate increase in bird abundance and diversity near edges, but | 115 | to moderate increase in bird abundance and diversity near edges, but | ||
| 116 | at the cost of losing presence of forest-demanding species playing | 116 | at the cost of losing presence of forest-demanding species playing | ||
| 117 | important ecological roles.", | 117 | important ecological roles.", | ||
| 118 | "es": "We examined interacting effects of habitat structure, | 118 | "es": "We examined interacting effects of habitat structure, | ||
| 119 | topographic landscape, road edge and vehicle traffic (density and | 119 | topographic landscape, road edge and vehicle traffic (density and | ||
| 120 | noise), on bird species composition, abundance and diversity in the | 120 | noise), on bird species composition, abundance and diversity in the | ||
| 121 | laurel forest of Tenerife (Canaries). We examined multivariate habitat | 121 | laurel forest of Tenerife (Canaries). We examined multivariate habitat | ||
| 122 | and landscape factors determining bird community composition and | 122 | and landscape factors determining bird community composition and | ||
| 123 | structure, and modality of specific responses by comparing road edge | 123 | structure, and modality of specific responses by comparing road edge | ||
| 124 | vs interior zones. Abundance of breeding birds in laurel forest showed | 124 | vs interior zones. Abundance of breeding birds in laurel forest showed | ||
| 125 | slight to no increases in response to roads. Two specialized taxa, the | 125 | slight to no increases in response to roads. Two specialized taxa, the | ||
| 126 | palaeoendemic pigeon Columba bollii and Regulus regulus, revealed | 126 | palaeoendemic pigeon Columba bollii and Regulus regulus, revealed | ||
| 127 | neatest negative reductions in abundance near roads. Higher noise | 127 | neatest negative reductions in abundance near roads. Higher noise | ||
| 128 | levels, vegetation density, lower canopy closure and wood selective | 128 | levels, vegetation density, lower canopy closure and wood selective | ||
| 129 | extraction characterized roadsides. Most passerines showed moderate | 129 | extraction characterized roadsides. Most passerines showed moderate | ||
| 130 | affinity for forest edges and did not evidence decreases due to road | 130 | affinity for forest edges and did not evidence decreases due to road | ||
| 131 | proximity. The topographic landscape in these mountainous areas | 131 | proximity. The topographic landscape in these mountainous areas | ||
| 132 | strongly interacted with road edge effects to determine bird community | 132 | strongly interacted with road edge effects to determine bird community | ||
| 133 | structure. Narrow road disturbances on the laurel forest was related | 133 | structure. Narrow road disturbances on the laurel forest was related | ||
| 134 | to moderate increase in bird abundance and diversity near edges, but | 134 | to moderate increase in bird abundance and diversity near edges, but | ||
| 135 | at the cost of losing presence of forest-demanding species playing | 135 | at the cost of losing presence of forest-demanding species playing | ||
| 136 | important ecological roles." | 136 | important ecological roles." | ||
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| 235 | 27.64]]]}", | 235 | 27.64]]]}", | ||
| 236 | "spatial_coverage": [ | 236 | "spatial_coverage": [ | ||
| 237 | { | 237 | { | ||
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| 242 | -18.16, | 242 | 35.715]}", | ||
| 243 | 27.64 | ||||
| 244 | ], | ||||
| 245 | [ | ||||
| 246 | 4.32, | ||||
| 247 | 27.64 | ||||
| 248 | ], | ||||
| 249 | [ | ||||
| 250 | 4.32, | ||||
| 251 | 43.79 | ||||
| 252 | ], | ||||
| 253 | [ | ||||
| 254 | -18.16, | ||||
| 255 | 43.79 | ||||
| 256 | ], | ||||
| 257 | [ | ||||
| 258 | -18.16, | ||||
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| 263 | "type": "Polygon" | ||||
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| 267 | -6.92, | ||||
| 268 | 35.715 | ||||
| 269 | ], | ||||
| 270 | "type": "Point" | ||||
| 271 | }, | ||||
| 272 | "text": "Espa\u00f1a", | 243 | "text": "Espa\u00f1a", | ||
| 273 | "uri": | 244 | "uri": | ||
| 274 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 245 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 275 | } | 246 | } | ||
| 276 | ], | 247 | ], | ||
| 277 | "spatial_resolution_in_meters": "", | 248 | "spatial_resolution_in_meters": "", | ||
| 278 | "spatial_uri": | 249 | "spatial_uri": | ||
| 279 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 250 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 280 | "state": "active", | 251 | "state": "active", | ||
| 281 | "study_variables": { | 252 | "study_variables": { | ||
| 282 | "es": "" | 253 | "es": "" | ||
| 283 | }, | 254 | }, | ||
| 284 | "tag_uri": [ | 255 | "tag_uri": [ | ||
| 285 | 256 | ||||
| 286 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 257 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 287 | ], | 258 | ], | ||
| 288 | "tags": [ | 259 | "tags": [ | ||
| 289 | { | 260 | { | ||
| 290 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | 261 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 291 | "id": "2379c860-0540-450a-9a23-72454ee80469", | 262 | "id": "2379c860-0540-450a-9a23-72454ee80469", | ||
| 292 | "name": "aspectos-globales-sobre-fragmentacion-de", | 263 | "name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 293 | "state": "active", | 264 | "state": "active", | ||
| 294 | "vocabulary_id": null | 265 | "vocabulary_id": null | ||
| 295 | }, | 266 | }, | ||
| 296 | { | 267 | { | ||
| 297 | "display_name": "fragmentacion", | 268 | "display_name": "fragmentacion", | ||
| 298 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 269 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 299 | "name": "fragmentacion", | 270 | "name": "fragmentacion", | ||
| 300 | "state": "active", | 271 | "state": "active", | ||
| 301 | "vocabulary_id": null | 272 | "vocabulary_id": null | ||
| 302 | } | 273 | } | ||
| 303 | ], | 274 | ], | ||
| 304 | "thematic_area": [ | 275 | "thematic_area": [ | ||
| 305 | "especies_silvestres" | 276 | "especies_silvestres" | ||
| 306 | ], | 277 | ], | ||
| 307 | "theme_es": [ | 278 | "theme_es": [ | ||
| 308 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 279 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 309 | ], | 280 | ], | ||
| 310 | "title": "Bird community structure and species responses to edges in | 281 | "title": "Bird community structure and species responses to edges in | ||
| 311 | laurel forest fragmented by narrow roads (Tenerife, Canary Islands).", | 282 | laurel forest fragmented by narrow roads (Tenerife, Canary Islands).", | ||
| 312 | "title_translated": { | 283 | "title_translated": { | ||
| 313 | "en": "", | 284 | "en": "", | ||
| 314 | "es": "Bird community structure and species responses to edges in | 285 | "es": "Bird community structure and species responses to edges in | ||
| 315 | laurel forest fragmented by narrow roads (Tenerife, Canary Islands)." | 286 | laurel forest fragmented by narrow roads (Tenerife, Canary Islands)." | ||
| 316 | }, | 287 | }, | ||
| 317 | "topic": | 288 | "topic": | ||
| 318 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 289 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 319 | "type": "dataset", | 290 | "type": "dataset", | ||
| 320 | "url": | 291 | "url": | ||
| 321 | //iepnb.es:443/catalogo/dataset/57216bd8-53d0-54c8-b5ee-29800053c085", | 292 | //iepnb.es:443/catalogo/dataset/57216bd8-53d0-54c8-b5ee-29800053c085", | ||
| 322 | "version": "", | 293 | "version": "", | ||
| 323 | "version_notes": { | 294 | "version_notes": { | ||
| 324 | "en": "", | 295 | "en": "", | ||
| 325 | "es": "" | 296 | "es": "" | ||
| 326 | } | 297 | } | ||
| 327 | } | 298 | } |